WO2012023300A1 - エアレーション装置及びこれを備えた海水排煙脱硫装置 - Google Patents
エアレーション装置及びこれを備えた海水排煙脱硫装置 Download PDFInfo
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- WO2012023300A1 WO2012023300A1 PCT/JP2011/054542 JP2011054542W WO2012023300A1 WO 2012023300 A1 WO2012023300 A1 WO 2012023300A1 JP 2011054542 W JP2011054542 W JP 2011054542W WO 2012023300 A1 WO2012023300 A1 WO 2012023300A1
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- Prior art keywords
- seawater
- aeration
- air
- slit
- treatment layer
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/46—Removing components of defined structure
- B01D53/48—Sulfur compounds
- B01D53/50—Sulfur oxides
- B01D53/501—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound
- B01D53/504—Sulfur oxides by treating the gases with a solution or a suspension of an alkali or earth-alkali or ammonium compound characterised by a specific device
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
- B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
- B01F23/20—Mixing gases with liquids
- B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
- B01F23/231—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
- B01F23/23105—Arrangement or manipulation of the gas bubbling devices
- B01F23/2311—Mounting the bubbling devices or the diffusers
- B01F23/23113—Mounting the bubbling devices or the diffusers characterised by the disposition of the bubbling elements in particular configurations, patterns or arrays
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
- B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
- B01F23/20—Mixing gases with liquids
- B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
- B01F23/231—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
- B01F23/23105—Arrangement or manipulation of the gas bubbling devices
- B01F23/2312—Diffusers
- B01F23/23124—Diffusers consisting of flexible porous or perforated material, e.g. fabric
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
- B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
- B01F23/20—Mixing gases with liquids
- B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
- B01F23/231—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
- B01F23/23105—Arrangement or manipulation of the gas bubbling devices
- B01F23/2312—Diffusers
- B01F23/23128—Diffusers having specific properties or elements attached thereto
- B01F23/231283—Diffusers having specific properties or elements attached thereto having elements to protect the parts of the diffusers, e.g. from clogging when not in use
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/74—Treatment of water, waste water, or sewage by oxidation with air
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2252/00—Absorbents, i.e. solvents and liquid materials for gas absorption
- B01D2252/10—Inorganic absorbents
- B01D2252/103—Water
- B01D2252/1035—Sea water
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01F—MIXING, e.g. DISSOLVING, EMULSIFYING OR DISPERSING
- B01F23/00—Mixing according to the phases to be mixed, e.g. dispersing or emulsifying
- B01F23/20—Mixing gases with liquids
- B01F23/23—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids
- B01F23/231—Mixing gases with liquids by introducing gases into liquid media, e.g. for producing aerated liquids by bubbling
- B01F23/23105—Arrangement or manipulation of the gas bubbling devices
- B01F23/2312—Diffusers
- B01F23/23126—Diffusers characterised by the shape of the diffuser element
- B01F23/231265—Diffusers characterised by the shape of the diffuser element being tubes, tubular elements, cylindrical elements or set of tubes
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/18—Nature of the water, waste water, sewage or sludge to be treated from the purification of gaseous effluents
Definitions
- the present invention relates to wastewater treatment of flue gas desulfurization equipment applied to power plants such as coal-fired, crude oil-fired, and heavy oil-fired, and in particular, wastewater of exhaust gas desulfurization equipment that uses the seawater method (used seawater).
- the present invention relates to an aeration apparatus for decarbonating (aeration) by aeration and a seawater flue gas desulfurization apparatus equipped with the aeration apparatus.
- combustion exhaust gas (hereinafter referred to as “gas”) discharged from a boiler is sulfur such as sulfur dioxide (SO 2 ) contained in the exhaust gas.
- SO 2 sulfur dioxide
- SOx oxide
- a desulfurization method of a flue gas desulfurization apparatus that performs such a desulfurization treatment, a limestone gypsum method, a spray dryer method, a seawater method, and the like are known.
- the flue gas desulfurization apparatus (hereinafter referred to as “seawater flue gas desulfurization apparatus”) employing the seawater method is a desulfurization system that uses seawater as an absorbent.
- a desulfurization tower (absorption tower) having a cylindrical shape such as a substantially cylindrical shape
- a wet-based gas-liquid contact is generated using seawater as an absorption liquid.
- SOTS Seawater Oxidation Treatment System
- SOTS Seawater Oxidation Treatment System
- the carbon dioxide is decarboxylated (explosion) by aeration that causes fine bubbles to flow out from the aeration apparatus installed in (Patent Documents 1 to 3).
- the aeration nozzle used in the aeration apparatus is one in which many small slits are provided in a diffused film made of rubber or the like covering the periphery of the base material. Generally, it is called “diffuser nozzle”. Such an aeration nozzle can cause a large number of fine bubbles of approximately the same size to flow out from the slit by the pressure of the supplied air. Conventionally, in the case of a rubber diffuser membrane, the length of the slit is about 1 to 3 mm.
- Precipitation occurs when seawater located outside the diffuser membrane soaks into the diffuser membrane from the slit, and constantly touches the air passing through the slit for a long time to dry (concentrate the seawater). ) Is promoted and presumed to be precipitated.
- an object of the present invention is to provide an aeration apparatus capable of suppressing and avoiding the generation of precipitates in a slit of a diffuser membrane and a seawater flue gas desulfurization apparatus including the aeration apparatus.
- a first invention of the present invention for solving the above-described problem is an aeration apparatus that is immersed in the water to be treated and generates fine bubbles in the water to be treated, and an air supply pipe that supplies air by discharge means; And an aeration nozzle having a diffuser membrane having a slit to which air is supplied, and having a water repellent treatment layer at an opening of the slit and / or in the vicinity thereof. .
- the second invention is the aeration apparatus according to the first invention, wherein the water repellent treatment layer is a coating treatment layer made of a hydrophobic material.
- a third invention is the aeration apparatus according to the first invention, wherein the water repellent treatment layer is any one of a fluorine coating treatment layer, a silicone coating treatment layer, and a wax coating treatment layer.
- a fourth invention is the aeration apparatus according to the first invention, wherein the water repellent treatment layer is a fractal structure treatment layer.
- the fifth invention is an aeration apparatus according to any one of the first to fourth inventions, wherein the diffuser membrane is made of rubber, metal or ceramics.
- a sixth invention is an aeration apparatus that is immersed in the water to be treated and generates fine bubbles in the water to be treated, and includes an air supply pipe that supplies air by a discharge means and a slit that is supplied with the air.
- An aeration nozzle provided with a gas film, and the gas diffusing film is formed by adding 25 to 95 parts by weight of a hydrophobic material to 100 parts by weight of the rubber material.
- An aeration apparatus having a water repellent treatment layer in the vicinity thereof.
- a seventh aspect of the invention is an aeration apparatus that is immersed in the water to be treated and generates fine bubbles in the water to be treated, and includes an air supply pipe that supplies air by a discharge means and a slit that is supplied with the air.
- An aeration apparatus comprising an aeration nozzle provided with an air film and a hydrophobic material supply means for adding a hydrophobic material to the air supply pipe.
- the eighth invention includes a desulfurization tower using seawater as an absorbent, a water channel for flowing and draining used seawater discharged from the desulfurization tower, and a fine bubble installed in the water channel.
- a seawater flue gas desulfurization apparatus comprising: first to seventh aeration apparatuses that perform decarboxylation by generating water.
- FIG. 1 is a schematic view of a seawater flue gas desulfurization apparatus according to the present embodiment.
- FIG. 2A is a plan view of the aeration nozzle.
- FIG. 2-2 is a front view of the aeration nozzle.
- FIG. 3 is a schematic diagram of the internal structure of the aeration nozzle.
- FIG. 4 is a schematic diagram of the aeration apparatus according to the present embodiment.
- FIG. 5 is a schematic view of an opening of a slit formed in the diffuser film of the aeration nozzle according to the present embodiment.
- FIG. 6A is a diagram illustrating the state of outflow of air (humid air with low saturation), intrusion of seawater, and concentrated seawater in the slit of the diffuser membrane.
- FIG. 1 is a schematic view of a seawater flue gas desulfurization apparatus according to the present embodiment.
- FIG. 2A is a plan view of the aeration nozzle.
- FIG. 6-2 is a diagram showing the state of outflow of air, intrusion of seawater, concentrated seawater and precipitates in the slit of the diffuser membrane.
- FIG. 6-3 is a diagram illustrating the state of air outflow and seawater intrusion, concentrated seawater, and precipitates (when the precipitates grow) in the slit of the diffuser membrane.
- FIG. 7 is a schematic view of another aeration apparatus according to the present embodiment.
- FIG. 8 is an example of a schematic diagram of a fractal structure.
- FIG. 9 is a chart obtained by analyzing precipitates by X-ray diffraction.
- FIG. 1 is a schematic view of a seawater flue gas desulfurization apparatus according to the present embodiment. As shown in FIG. 1
- a seawater flue gas desulfurization apparatus 100 includes a flue gas desulfurization absorption tower 102 that makes a gas-liquid contact between exhaust gas 101 and seawater 103 to desulfurize SO 2 to sulfurous acid (H 2 SO 3 ),
- a dilution mixing tank 105 is provided below the smoke desulfurization absorption tower 102 to dilute and mix the used seawater 103A containing sulfur with the seawater 103 for dilution, and is provided downstream of the dilution mixing tank 105 for use in dilution. It comprises an oxidation tank 106 that performs a water quality recovery process of the finished seawater 103B.
- seawater flue gas desulfurization apparatus 100 a part of the seawater 103 for absorption in the seawater 103 supplied through the seawater supply line L 1 in the flue gas desulfurization absorption tower 102 is brought into gas-liquid contact with the exhaust gas 101, thereby SO 2 in 101 is absorbed by seawater 103. And the used seawater 103A which absorbed the sulfur content with the flue gas desulfurization absorption tower 102 is mixed with the seawater 103 for dilution supplied to the dilution mixing tank 105 provided in the lower part of the flue gas desulfurization absorption tower 102.
- reference numeral 102 a is a spray nozzle for a liquid column that ejects seawater upward
- 120 is an aeration device
- 122 a is air bubbles
- L 1 is a seawater supply line
- L 2 is a diluted seawater supply line
- L 3 is a desulfurized seawater supply.
- L, L 4 is an exhaust gas supply line
- L 5 is an air supply line.
- FIG. 2-1 is a plan view of the aeration nozzle
- FIG. 2-2 is a front view of the aeration nozzle
- FIG. 3 is a schematic diagram of the internal structure of the aeration nozzle.
- the aeration nozzle 123 has a rubber diffuser film 11 covering the periphery of a base material and is provided with many small slits 12. It is called a “diffuser nozzle”.
- the aeration nozzle 123 can open a large number of fine bubbles of substantially equal size when the diffuser membrane 11 is expanded by the pressure of the air 122 supplied from the air supply line L 5 and the slit 12 is opened. .
- FIG 2-1 as shown in Figure 2-2, aeration nozzles 123, the header 15 provided in the branch pipe of the plurality of branched from the air supply line L 5 (8 in this embodiment) (not shown) On the other hand, it is attached via a flange 16.
- a resin pipe or the like is used for the branch pipe and header 15 installed in the diluted used seawater 103B in consideration of corrosion resistance.
- the aeration nozzle 123 uses a substantially cylindrical support 20 made of resin in consideration of the corrosion resistance against diluted used seawater 103 ⁇ / b> B, and many aeration nozzles 123 cover the outer periphery of the support 20. After covering the rubber diffuser film 11 in which the slits 12 are formed, the left and right ends are fixed by fastening members 22 such as wires and bands.
- the above-described slit 12 is closed in a normal state where no pressure is applied.
- the slit 12 is always open.
- the one end 20a of the support body 20 is capable of introducing the air 122 in a state of being attached to the header 15, and the other end 20b is opened so that the seawater 103 can be introduced.
- the one end 20 a side communicates with the inside of the header 15 through the air introduction port 20 c that penetrates the header 15 and the flange 16.
- the inside of the support body 20 is divided
- the air diffuser 11 is pressurized and expanded between the inner peripheral surface of the diffuser membrane 11 and the outer peripheral surface of the support. Air outlets 20e and 20f for allowing the air 122 to flow out into the pressurized space 11a are opened. Therefore, the air 122 flowing into the aeration nozzle 123 from the header 15 flows into the inside of the support 20 from the air inlet 20c and then is pressurized from the side air outlets 20e and 20f as shown by arrows in the drawing. It will flow out to 11a.
- the fastening member 22 fixes the diffuser membrane 11 to the support 20 and prevents air flowing in from the air outlets 20e and 20f from leaking out from both ends.
- the air 122 flowing from the header 15 through the air introduction port 20c flows out to the pressurized space 11a through the air outlets 20e and 20f, so that the slit 12 is initially formed. Since it is closed, it accumulates in the pressurizing space 11a and raises the internal pressure. As a result of the increase in the internal pressure, the diffuser membrane 11 expands upon receiving a pressure increase in the pressurized space 11a, and the slits 12 formed in the diffuser membrane 11 are opened to dilute and use fine bubbles in the air 122. It flows out into the seawater 103B.
- FIG. 4 is a schematic diagram of the aeration apparatus according to the present embodiment.
- the aeration apparatus 120 according to the present embodiment is an aeration apparatus that is immersed in diluted used seawater (not shown) that is water to be treated and generates fine bubbles in the diluted used seawater.
- the air supply line L 5 for supplying the air 122 by the blowers 121A to 121D serving as the discharge means and the aeration nozzle 123 having the diffuser film 11 having the slit to which the air is supplied are provided.
- the air supply line L 5 is provided with two coolers 131A and 131B and two filters 132A and 132B.
- the air compressed by the blowers 121A to 121D is cooled and then filtered.
- the cooled and filtered air is supplied by all aeration nozzles 123 that receive air supply through the branch pipes L 5A to 5H and the header 15, and fine bubbles are generated.
- the four blowers are usually operated with three blowers, one of which is reserved. Also, the reason why there are two each of the coolers 131A and 131B and the filters 132A and 132B is that they need to be operated continuously, so that usually only one is operated and the other is used for maintenance.
- FIG. 5 schematically shows the opening of the slit 12 formed in the diffuser membrane 11 of the aeration nozzle 123 according to this embodiment.
- the slit 12 has a water repellent treatment layer 150 formed on the slit wall surface 12a of the opening and the edge 12b of the opening. As described above, by subjecting the opening and the vicinity thereof to water repellent treatment, precipitation of precipitates can be suppressed and avoided.
- the salinity of seawater is 3.4%, and 3.4% salt is dissolved in 96.6% water.
- This salt is 77.9% sodium chloride, 9.6% magnesium chloride, 6.1% magnesium sulfate, 4.0% calcium sulfate, 2.1% potassium chloride, and 0.2% other It has a configuration.
- calcium sulfate is the first salt to be precipitated as the seawater is concentrated (seawater is dried), and the threshold for precipitation is about 14% in the salt concentration of seawater.
- FIG. 9 is a chart obtained by analyzing precipitates by X-ray diffraction. As shown in FIG. 9, it was found that most of the peaks were derived from calcium sulfate.
- FIG. 6A is a diagram illustrating the state of outflow of air (humid air with low saturation), intrusion of seawater, and concentrated seawater in the slit of the diffuser membrane.
- FIG. 6B is a diagram illustrating the state of air outflow, seawater intrusion, concentrated seawater, and precipitates in the slit of the diffuser membrane.
- FIG. 6-3 is a diagram illustrating the state of air outflow and seawater intrusion, concentrated seawater, and precipitates (when the precipitates grow) in the slit of the diffuser membrane.
- the slit 12 refers to a cut formed in the diffuser membrane 11, and the gap between the slits 12 serves as a passage through which air is discharged.
- the slit wall surface 12a forming this passage is in contact with the seawater 103, but is dried and concentrated by the introduction of air 122 to become the concentrated seawater 103a, and then the precipitate 103b is deposited on the slit wall surface, thereby closing the slit passage. Will be.
- FIG. 6A shows a situation in which the concentration of seawater salt is gradually increased and the concentrated seawater 103a is formed because the relative humidity (saturation) of the air 122 is low.
- concentration of seawater begins, precipitation of calcium sulfate or the like does not occur when the salt concentration of seawater is approximately 14% or less.
- FIG. 6-2 shows a state in which the precipitate 103b is generated in a part of the concentrated seawater 103a where the salinity of the seawater exceeds 14%.
- the pressure loss when the air passes through the slit 12 slightly increases, but the air 122 can pass therethrough.
- FIG. 6-3 shows a state where as the concentration of the concentrated seawater 103a progresses, the precipitate 103b becomes plugged (plugging) and the pressure loss increases. Even in such a state, although the passage of the air 122 remains, a considerable load is applied to the discharge means. Therefore, in order to prevent such a state, by providing the water repellent treatment layer 150 at the opening of the slit 12 and in the vicinity thereof, the intrusion of seawater into the slit is prevented, and the precipitate 103b is generated in the slit. Since it can be suppressed and avoided, stable operation over a long period of time becomes possible.
- Examples of the material for forming the water-repellent treatment layer include various water-repellent materials.
- a coating treatment layer made of a hydrophobic material using talc, silica powder, etc. a fluorine coating treatment layer coated with a fluororesin And a silicone coating layer coated with a silicone resin and a wax coating layer coated with a wax.
- a fixing agent that does not immediately peel off when the hydrophobic material is coated. What is necessary is just to make it form when releasing a diffuser film or after that.
- the surface state is hydrophobic and water is repelled. Therefore, intrusion of seawater into the slit is suppressed and avoided, the sea salt concentration of seawater is not concentrated, and precipitation of precipitates is prevented.
- FIG. 8 is a schematic diagram of a fractal structure.
- the surface of the slit may be a fractal structure treatment layer in which an infinite number of physical irregularities are formed, so that the water repellency may be improved.
- This fractal structure has a concavo-convex structure such as a Koch curve, which has a small ruggedness in a large ruggedness, and a smaller ruggedness in the small ruggedness. The one that increases the nature.
- an infinite number of uneven surfaces may be formed in the opening by, for example, forming the opening by plasma treatment. At this time, it is preferable to perform the treatment in an inert atmosphere. This is to prevent the generation of oxygen functional groups.
- the diffuser membrane is preferably made of rubber, but the present invention is not limited to this, and examples thereof include stainless steel and resin.
- fluororesin examples include polytetrafluoroethylene (tetrafluorinated resin, abbreviation: PTFE), polychlorotrifluoroethylene (trifluorinated resin, abbreviation: PCTFE, CTFE), polyvinylidene fluoride (abbreviation: PVDF), and polyfluoride.
- PTFE polytetrafluoroethylene
- PCTFE polychlorotrifluoroethylene
- CTFE trifluorinated resin
- PVDF polyvinylidene fluoride
- PVF Vinyl
- PFA perfluoroalkoxy fluororesin
- FEP tetrafluoroethylene / hexafluoropropylene copolymer
- ETFE ethylene / tetrafluoroethylene copolymer
- ECTFE chlorotrifluoroethylene copolymer
- a hydrophobic material in the diffuser film 11 itself.
- 25 to 95 parts by weight of a hydrophobic material is added to 100 parts by weight of the rubber material to form a diffuser film, and as a result, a water repellent treatment layer is provided at the opening of the slit 12 and / or in the vicinity thereof. It may be. If the addition of the hydrophobic material is outside the above range, the water repellency effect cannot be exhibited, which is not preferable.
- the hydrophobic material include talc and silica powder, but the present invention is not limited thereto.
- the rubber material is preferably ethylene-propylene-diene rubber (EPDM).
- FIG. 7 is a schematic view of another aeration apparatus according to the present embodiment.
- the aeration apparatus 120A according to the present embodiment is provided with a hydrophobic material supply means 161 for adding the hydrophobic material 160 to the aeration apparatus 120 shown in FIG. 4, via the hydrophobic material line L 6 .
- the hydrophobic material 160 is supplied into the air supply line L 5 .
- the hydrophobic material 160 to be added for example, it is preferable to use at least one of talc and silica powder.
- the supply of the hydrophobic material 160 is performed by removing precipitates from the slit 12 after the pressure fluctuates when air 122 is supplied and fine air is supplied from the aeration nozzle 123, and then water repellent treatment is performed. Is preferably performed.
- the deposits may be removed by performing an air purging process or an air stopping process to change the slits 12 of the diffuser film 11 and remove the deposits attached to the slits 12. By performing this water repellency treatment, the slit 12 has water repellency and is less likely to become dirty.
- seawater is taken as an example of the water to be treated in the present embodiment, but the present invention is not limited to this.
- Plugging due to the deposition of sludge components in step (3) can be prevented, and stable operation can be achieved over a long period of time.
- the tube type aeration nozzle is used as the aeration apparatus.
- the present invention is not limited to this.
- the disk type or flat plate aeration apparatus ceramics, metal (for example, It can be applied to a diffuser made of stainless steel.
- the aeration apparatus of the present invention it is possible to suppress and avoid the generation of precipitates in the slits of the diffuser membrane of the aeration apparatus. As a result, continuous and stable operation is possible.
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CN201180031466.2A CN102958846B (zh) | 2010-08-18 | 2011-02-28 | 通风装置及具备该装置的海水烟气脱硫装置 |
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JP2010183500A JP5535824B2 (ja) | 2010-08-18 | 2010-08-18 | エアレーション装置及びこれを備えた海水排煙脱硫装置 |
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JP (1) | JP5535824B2 (ar) |
CN (2) | CN102958846B (ar) |
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SA (1) | SA111320563B1 (ar) |
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AT516115A1 (de) * | 2014-07-24 | 2016-02-15 | Ecoduna Ag | Verfahren für einen photochemischen, wie photokatalytischen und/oder photosynthetischen, Prozess |
JP2020175343A (ja) * | 2019-04-19 | 2020-10-29 | 株式会社超微細科学研究所 | エアレータ |
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JP3149970B2 (ja) * | 1991-08-06 | 2001-03-26 | ジャパンゴアテックス株式会社 | 散気材及びそれを用いたガスの散気方法 |
JP3498402B2 (ja) * | 1995-02-06 | 2004-02-16 | 石川島播磨重工業株式会社 | 脱硫装置 |
DE602006020656D1 (de) * | 2005-05-18 | 2011-04-28 | Thomas Edward Frankel | Verfahren zur Herstellung einer Kompositmembran mit dünner fluorhaltiger Polymerschicht |
US7674514B2 (en) * | 2005-12-02 | 2010-03-09 | Thomas E Frankel | Multiple layered membrane with thin fluorine containing polymer layer |
JP5259964B2 (ja) * | 2007-02-28 | 2013-08-07 | 三菱重工業株式会社 | 海水排煙脱硫システム |
JP5072470B2 (ja) * | 2007-07-24 | 2012-11-14 | 三菱重工業株式会社 | エアレーション装置 |
CN101732961A (zh) * | 2008-11-27 | 2010-06-16 | 何刚 | 一种海水脱硫工艺 |
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2010
- 2010-08-18 JP JP2010183500A patent/JP5535824B2/ja active Active
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2011
- 2011-02-28 MY MYPI2012701228A patent/MY161508A/en unknown
- 2011-02-28 CN CN201180031466.2A patent/CN102958846B/zh active Active
- 2011-02-28 WO PCT/JP2011/054542 patent/WO2012023300A1/ja active Application Filing
- 2011-02-28 CN CN201510089199.4A patent/CN104707496B/zh active Active
- 2011-04-29 TW TW100115183A patent/TWI523818B/zh active
- 2011-06-29 SA SA111320563A patent/SA111320563B1/ar unknown
- 2011-08-11 US US13/207,509 patent/US20120042784A1/en not_active Abandoned
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JPH02229590A (ja) * | 1989-03-02 | 1990-09-12 | Toray Ind Inc | 水処理方法 |
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JP2003144868A (ja) * | 2001-11-08 | 2003-05-20 | Korea Res Inst Of Chem Technol | 超撥水性有機/無機複合膜 |
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Also Published As
Publication number | Publication date |
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TW201213245A (en) | 2012-04-01 |
CN102958846A (zh) | 2013-03-06 |
CN102958846B (zh) | 2015-08-26 |
JP2012040494A (ja) | 2012-03-01 |
CN104707496B (zh) | 2017-07-07 |
JP5535824B2 (ja) | 2014-07-02 |
TWI523818B (zh) | 2016-03-01 |
US20120042784A1 (en) | 2012-02-23 |
SA111320563B1 (ar) | 2014-10-15 |
MY161508A (en) | 2017-04-28 |
CN104707496A (zh) | 2015-06-17 |
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